Select Committee on Environment, Transport and Regional Affairs Memoranda


MEMORANDUM BY SURREY COUNTY COUNCIL (DSW 92)

1.  GENERAL

  Surrey County Council is at the forefront of local authority waste management contracting having been awarded Private Finance Initiative funding of £100m for its integrated waste management contract awarded in 1999. The contract is for one billion pounds over 25 years. It was conceived in a context of joint working between two-tier waste authorities and recognises that only by integrating the contribution of the private sector within a local authority partnership framework will any real progress be made towards achieving sustainable waste management.

  The structure of the contract recognises and gives effect to the realisation that only through the use of incineration, whether combined heat and power or energy recovery, will the diversion rates from landfill, which will be a legally binding obligation on the UK, be achieved. It recognises that a balance between waste management options has to be struck in order to obtain the political and public support that is needed in order to avoid virtual total reliance on incineration as the only practical waste management option.

  The contract was conceived within the framework of a Way With Waste. In its last report on waste management, the committee noted that "waste management in this country is still characterised by inertia, careless administration, and ad hoc, rather than science based, decisions." The lessons from this contract, which is less than one year into its term, indicate that possibly inertia is a safer attitude than action when one is dealing with an administration in the government which has by its action demonstrated so little regard for the actual realities which confront local authorities.

  As a consequence of letting its contract to one of the largest waste management companies in Europe, and also one of the largest landfill operators on the UK, Surrey has conceived a singular relationship with the contractor's landfill tax Environmental Trust. Current planned disbursements within Surrey are approx £1 million per annum with at least 60 per cent earmarked for sustainable waste management purposes.

  The committee's investigation is under the title Delivering Sustainable Waste Management. In addition to the general questions being addressed, the committee has identified several particular issues that it wishes to examine. This evidence will focus on those issues as they affect Surrey and the management of the household waste stream. It will attempt to draw more general conclusions where it is felt safe to do so.

2.  EVIDENCE

  2.1  This will be addressed against the following specific context.

  (a)  The EU Council of Ministers have approved the landfill directive which the UK government has indicated that it will bring into effect by July 2001. It has stated that it will apply the four year derogation options.

  (b)  Government has stated that it sees the relationships between the two-tier authorities as a reason for poor progress towards the previous recycling targets which were set out in Making Waste Work.

  (c)  Government has indicated a national average increase in waste per annum in the region of three per cent and should therefore be able to utilise this with its data from the household waste survey to calculate future supply of recyclable materials when applied to its prescribed recycling targets.

  (d)  The government has recently published its proposals for setting targets etc. in its review of Best Value 2001/2002. These are taken to be actual, rather than aspirational, targets which was an issue upon which the committee focused in its last report.

  (e)  Surrey County Council in partnership with SITA Environmental Trust and the University of Surrey Environmental Body is participating in one of the largest issue-specific public attitude surveys into waste and residents' behavioural drivers undertaken.

  (f)  A land use planning framework which has each shire county determining its own waste land use policies.

2.2  More efficient use of resources and consequent reduction in the amount of waste entering the waste stream

  The precise thrust of this issue is a little unclear. Clearly manufacturers can obtain improved materials efficiencies, however, this does not of itself necessarily lead to reduced post-consumer waste volumes. If it takes only 50g of material as opposed to 100g to produce a product weighing 20g, the consumer and WDA are still faced with 20g, whereas the commercial sector has saved 50g.

  At this point I would like to address the issue of definitions. This is a matter of importance as a language is emerging which varies significantly from the terms used in Making Waste Work.

  This issue was highlighted when reading the evidence to and last report of this committee. Paragraph 198 states that as a WDA makes waste disposal savings in respect of materials recycled by a WCA "there would appear to be an incentive upon a WCA to encourage householders . . . to recycle." This might be true, but is unlikely. The WDA reimburses WCAs on the basis of disposal savings whereas the WCA incurs collection costs for recycling (including disposal of the material which should have positive value). There is no economic model yet produced which shows that these totally different services should have the same unit cost. "True" waste minimisation represents a reduction in the total waste handled by the WDA, and total saving, whereas recycling credits (the reimbursement from WDAs to WCAs) are a reward for disposing of something in a preferable environmental way.

  Neither is minimisation synonymous with diversion from landfill. Indeed, it can be seen differently depending on who is making the assessment:

  Waste minimisation:

    —  To a WDA— reduction in the amount of waste it handles under s51 of the EPA. Recycling is not minimisation but a form of disposal.

    —  To a WCA— reduction in the amount of waste it collects under s45.

  WDAs provide civic amenity sites and, by way of example, if a resident takes their household waste to one of these sites (at which it might be recycled) it is not collected by the WCA who therefore have no record of its existence. No waste has been minimised in total. CA sites are not based on the catchment areas of any single WCA and therefore it is true to say that which WCAs can assist with minimisation, only the WDA knows what is happening in total. Both have a power to promote waste minimisation (a matter recommended by the committee) however, funding is unclear.

  Another example of the confused thinking of government in this matter applies to home composting. Until 1999 WCAs could provide residents with home compostors and could count on assessed quantity of composting towards their recycling targets. WCAs therefore could see a return on their investment and less waste came into the waste stream, which pleased WDAs. Some WCAs abused the assessment process, however, the principle was sound even if practice created some problems.

  Subsequently, government decided that home composting would not count towards recycling levels. There is now no incentive. The waste management realities remain, however, and any waste not produced by a house eg disposed of on the property, is waste minimisation. WDAs still benefit from this by virtue of less waste but are prevented from incentivising their WCAs in financial terms. In addition, WDAs do not have powers to provide this equipment to residents.

  The government's proposals in the strategy regarding minimisation are unlikely to be as effective as they would wish because of a lack of understanding of roles of authorities and the barriers created by the existing financial system. Without such an understanding, motivation is unlikely. Funding mechanisms are unclear and potentially contradictory.

  Surrey has overcome some of these structural problems through its contract by placing the minimisation burden on the contractor as a transfer of risk under the PFI structure test. However, the future scale of PFI funding for waste, although sizeable, will deny this opportunity to most WDAs.

  When the Royal Commission on Local Government (Redcliffe Maud) investigated the allocation of local government functions it had a clear preference for unitary authorities. For various reasons this did not translate into a universal application. Nonetheless, unitary waste authorities, particularly London boroughs, claim to perform better by virtue of being responsible for all aspects of waste management. Something similar in shires might be necessary, however, other measures can and should be tried before this.

  It is suggested that the committee consider recommending to government:

    (a)  That WDAs have the primary waste minimisation responsibility.

    (b)  That WDAs are provided with the power to incentivise their WCAs financially.

    (c)  WCAs should be consulted as to whether the financial incentives should include an option for their WDA to charge them on a per tonne basis.

2.3  An increase in the recycling of waste, particularly by greater development of markets for recycled material

  The creation of WRAP is a positive move. However, recycling is a global business, as recent experiences with paper demonstrate. Congestion charging and improved public transport is another chicken and egg example of the problems that WRAP will face. The maintenance of balance as between supply (driven by government targets) and demand, in the context of consumer confidence, is difficult. In addition, we have a planning system which:

    (a)  require the shires to compile Waste Local Plans but which excludes from their scope processing plant such as glass factories, paper mills etc.

    (b)  in the context of economically-scaled processing capacity should be set at regional level, and

    (c)  finally places the authority to approve applications for such regional facilities with local district councils' development control departments.

  It will be difficult to make much headway in a short time in such a context.

2.4  Increased use of incineration as a waste disposal/recovery option—what would the implications of this be.

  Incineration is an alternative to landfill, not recycling.

  Government has danced around this issue, even to the extent that its stance on incineration changed so dramatically between the draft strategy and final version. This was a political and not waste management decision. It is not invalid because of this, however, their subsequent pronouncements render the government duplicitous in some people's eyes.

  The government's use of its derogation rights under the landfill directive comes about only because we landfill so much of our waste— 90 per cent plus of household waste. Clearly there is a tension between the mathematical and waste management realities and political needs. However, sustainable waste management does not lend itself to short term expedient political decision-making.

  The government has indicated a major shift away from incineration in the Waste Strategy and reinforced this by excluding from the definition of recycling the re-use of incinerator bottom ash, something that it specifically included in the previous definition.

  Surrey County Council took a bold step with its contract that took its lead from the government's stance in the draft strategy. It therefore took a science-based pragmatic approach to waste management. It was guided by overwhelming private sector views which were canvassed during the contracting process. Consequently, it relies heavily on incineration. It is flexible. However, the need to demonstrate this to such a degree so early in its term has come as something of a surprise.

  The concerns regarding incineration are real and it would be foolish to underestimate them. Primarily they fall into two distinct camps—air quality and traffic. Traffic is a local factor and will be judged on a case by case basis. Air quality is different. The government is again acting in a contradictory fashion here.

  It is government agencies which advise on and set emission limits, and which grant pollution control authorisations. However, they are not responsible for national waste management, government is. While there has been a shift in the government's stance on a political level and in the strategy, there is no evidence that it is grasping the nettle of air quality with a view to promoting a science-based approach to this. Essentially local authorities will be gradually worn down if the hearts and minds issues are not dealt with nationally.

  As regards the implications of an increase in incineration, it is felt that an increase should not necessarily lead to the abandonment of recycling, as these can co-exist. If necessary, WDAs can be given recycling and energy recovery ratios to replace current recycling targets. It is felt unlikely that the necessary increase to meet the landfill directive diversion rates can be met within the current waste planning regime which is in need of urgent review.

  Referring again to the Royal Commission, one of its aims was to deal with matters so as to take them off the agenda for a considerable time. The issue of public confidence regarding incineration needs to be faced, dealt with and taken off the agenda for a considerable time.

2.5  A reduction in the amount of waste sent to landfill

  Currently some authorities are reporting increases in waste of over 5 per cent p.a. Even if the national average is 3 per cent the mathematical reality is that this growth will not translate into a reduction in landfill even if the target for 2004 (average of 17 per cent recycling nationally) is met. This will occur, however, if the 2005 target is met. At the same time there is a considerable body of opinion which suggests that the 25 per cent level is unlikely to be achieved. Therefore in the short term (four years) the best that can be hoped for is a reduction in the rate of increase.

  If a reduction could be achieved through waste minimisation and recycling, this would be a great success. It still leaves the waste reality that over 50 per cent of waste remains to be dealt with by other means. There appears to be no way of escaping this reality and the two options available: landfill and incineration.

  As regards the tax credits scheme (LFTCS), Surrey is partnering with its main contractor, SITA, all districts and other voluntary groups the creation of a fund to be disbursed through the Sustainable Surrey Forum. This will have effect in all project categories. The government has given a clear, strong and welcome lead here regarding its preferred use of funds and Surrey will take this on board. Surrey County Council, its WCAs are currently recycling 17 per cent and would hope to drive this upwards through partners. Significantly, some of the local government barriers referred to earlier regarding waste minimisation and incentivisation can be overcome by such partnerships using LFTCS funds. The Forum will look to develop a medium term plan and in this respect the recycling target dates of 2004 and 2005 do not sit well with a guaranteed LFTCS period ending in 2004.

  As regards the Forum, it has developed a range of sustainability indicators, some of which involve waste. Whereas government Performance Indicators tend to focus on the obvious, others being looked at seek to challenge conventional wisdom. One of these involves assessing waste management sustainability by reference to emissions (CO2 etc) per tonne mile travelled by waste. This naturally leads to an holistic approach which, for example, challenges the need for civic amenity sites as WCAs are able to collect all materials in a way which gives improved environmental benefits. This will lead to cost benefit analysis of removing these sites from the waste system (and two million + vehicle journeys per annum by residents who use the sites) and whether in countrywide environmental terms this is a better option than the current system. The ability to reimburse WCAs would be necessary and has been raised earlier as an issue.

  Primarily, and rightly, LFTCS should fund capital eg recycling boxes, vehicles etc. Surrey's contract enables the primary revenue risk to be dealt with by the contractor. It is understood that the possibility of using LFTCS for large-scale capital assets eg processing plant etc has not been explored, although LFTCS have been used for buildings in other project categories. The need for logistical balance as between supply, processing capacity and demand still remains. In light of the funding priorities which the government has now set, the scheme's objects should be reviewed to ensure that the development of large-scale assets is possible for category c projects.

  In addition, a clear steer regarding the continuation of the scheme is necessary to enable coherent planning over the medium term.

2.6  A reduction in and better management of hazardous wastes

  No evidence to submit here.

2.7  Significant action to improve the example set by government in exercising "green" procurement policies.

  All responsible authorities, particularly public, should endeavour to practise what they preach. This sends out correct messages and gives leadership, particularly when others are expected to make changes to their habits, lifestyle etc. This can be seen as being a form of community leadership and is an important role for government and local authorities. However, in this context and it is not considered the key one. This remains to properly assess, plan and put in place the necessary structure to enable the delivery of outcomes through others.,

2.8  Sufficient action to educate the public about the importance of sustainable waste management.

  This is an interesting point. When the committee last looked into this, one of its standard questions to witnesses was "what is your understanding of sustainable waste management". A range of answers was received. Witnesses who are experts in the field of waste management agreed that there is no single definition. In the context of this question, if they could not agree how could this concept be delivered to the public in a way that leads to beneficial changes in their behaviour.

  Also in the report there was evidence to suggest that the public were able to understand concepts and should not be talked down to. The combination of these factors will lead to interesting debate.

  Surrey's approach is clear. The task is redefined as "to inform the public about waste management issues of direct relevance to them which they are in a position to affect through their own actions". Clearly, we need to understand the behavioural drivers of individuals if progress is to be made. Evidence from various waste awareness campaigns shows some correlation exists between effort taken to publicise the message and people's recognition, but little between recognition and changes in habits. If the aim is to change people's attitudes then an understanding of how they think and act is crucial. In this context, Surrey County Council is supporting the University of Surrey Environmental Body in a project which it is conducting within Surrey using LFTCS from SITA Environmental Trust. The project will engage with over 15,000 residents to attempt to establish their behavioural drivers. These are unlikely to be totally Surrey-specific and therefore the results should enable improved waste management planning both in Surrey and elsewhere.

  This issue of education is distinct from the one raised earlier regarding the government informing the public regarding incineration. That does not need a change in action, simply an understanding and acceptance of what others want to do. The two tasks can be linked, but they are different.

  As regards the impact which the strategy will have on educating the public, much of this lies directly with WRAP. If they have sufficient funds then they can make some headway. However, as mentioned above, waste management is essentially about logistics: the balancing of expectation, supply, processing capacity and demand. To raise people's expectations (convincing millions to separate their recyclables) only to have these founder on the local reality when their WCA has no kerbside service will be disastrous. Local authorities are best placed to install the infrastructure and ensure that the process flows.

  WRAP will be best placed to articulate and lobby on behalf of authorities and government. They might also consider acting as a materials broker countrywide to ensure continuity of markets (although this smacks of the discredited DSD system which dumped, either on other countries or its own incinerators/landfill sites, tonnes of unwanted recyclables). Co-ordination is essential, as is understanding of the roles each party is best placed to play—which is to revisit one of the first points made regarding the government's apparent lack of understanding.


 
previous page contents next page

House of Commons home page Parliament home page House of Lords home page search page enquiries index

© Parliamentary copyright 2000
Prepared 24 October 2000